Process and device for devolatizing feedstock

ABSTRACT

Provided herein is a method, device and installation for devolatizing a solid feedstock, comprising carbon-based waste selected from the group consisting of hazardous material, biomass, animal manure, tires, municipal solid waste and refuse derived fuel. The method comprises treating the solid feedstock to a produce a particle size laying between about 1 cm 3  and about 100 cm 3 . The solid feedstock is passed into a jacketed system. The solid feedstock is contacted with a heated gas, comprising hydrogen, inside the jacketed system at a temperature of about 500° C. to about 1000° C. for a time of about 60 seconds to about 120 seconds, whereby the solid feedstock is converted into a gas stream and a solid stream.

RELATED APPLICATIONS

This application claims the benefit of priority of U.S. ProvisionalPatent Application No. 61/699,579, filed Sep. 11, 2012, the teachingsand contents of which are incorporated herein by reference.

FIELD OF THE INVENTION

The present disclosure generally relates to a process and device fordevolatizing a feedstock, in particular to a process and device forpyrolyzing or hydropyrolyzing a solid feedstock derived from one or morewaste materials.

BACKGROUND OF THE INVENTION

Pyrolysis refers to thermochemical decomposition of a solid feedstock,such as solid waste. Pyrolysis occurs at elevated temperatures withoutthe participation of oxygen. This decomposition is accompanied bydevolatization; that is, the escape of volatile gases from the solidfeedstock. Hydropyrolysis is a type of pyrolysis that occurs in ahydrogen-rich atmosphere. Both pyrolysis in general and hydropyrolysisin particular are important processes in waste-to-energy (WTE)conversion. Furthermore, pyrolytic processes typically generate twooutput streams: a gas stream and a solid stream

Most WTE systems are through-systems, where waste is combined with fuelas required and then burned. For example, in a typical 50 megawatt (MW)incinerator plant, approximately 5,000 tons of waste may be burnt perday. Unfortunately, about 50% to about 60% of the waste processed istransformed into incompletely burned bottom ash, which has to be sent toa landfill. Additionally, fly ash is produced, which is classified ashazardous waste and must be processed as such. Burning raw municipalsolid waste (MSW) also creates heavy metal emissions, especially fromburning plastics, aluminum and batteries contained in a general unsortedwaste stream. An expensive and complex off-gas treatment installation isnecessary to reduce these emissions to levels required to meetenvironmental and other regulations. Also, if the MSW is wet, itgenerally costs more in energy to burn the waste than the actual amountof energy produced from the waste.

Moreover, typical pyrolytic processes only use indirect heating tocreate pyrolytic conditions, but having enough heat transfer from thepyrolytic device to the feedstock poses numerous operational issues. Toovercome these limitations, longer travel paths for the feedstock havebeen implemented. Increased travel paths, however, increase the time ofconversion and device size. As a result, process efficiency and deviceportability are diminished. The process takes longer and requiresgreater energy input. Thus, these pyrolytic processes have gas emissionswhich are unacceptable for current standards in many jurisdictions, areneedlessly bulky and inefficient.

SUMMARY OF THE INVENTION

Provided herein is a method for devolatizing a solid feedstock,comprising carbon-based waste selected from the group consisting ofhazardous material, biomass, animal manure, tires, municipal solid wasteand refuse derived fuel. The method comprises treating the solidfeedstock to a produce a particle size laying between 1 cm³ and 100 cm³.The method further comprises passing the solid feedstock into a jacketedsystem. The next step of the method comprises contacting the solidfeedstock with a heated gas, comprising hydrogen, inside the jacketedsystem at a temperature of about 500° C. to about 1000° C. for a time ofabout 60 seconds to about 120 seconds, whereby the solid feedstock isconverted into a gas stream and a solid stream.

In other embodiments, the present disclosure provides a method of usinga heated gas, comprising hydrogen, to pyrolyze a solid feedstock,comprising carbon-based waste selected from the group consisting ofhazardous material, biomass, animal manure, tires, municipal solid wasteand refuse derived fuel. The method comprises treating the solidfeedstock to a produce a particle size laying between 2 cm³ and 3 cm³.The method further comprises passing the solid feedstock into a jacketedsystem. The next step of the method comprises contacting the solidfeedstock with the heated gas inside the jacketed system at atemperature of about 800° C. to about 900° C. and a pressure of about0.5 atm to about 2 atm for a time of about 60 seconds to about 120seconds, whereby the solid feedstock is converted to a gas stream and asolid stream.

In yet other embodiments, the present disclosure provides aninstallation for pyrolyzing a solid feedstock, comprising waste selectedfrom the group consisting of hazardous material, biomass, animal manure,tires, municipal solid waste and refuse derived fuel. The installationcomprises a device for reducing particle size, a compaction screw auger,a device for contacting the solid feedstock with a heated gas,comprising hydrogen gas, inside a jacketed system at a temperature ofabout 500° C. to about 1000° C. for a time of about 60 seconds to about120 seconds, whereby the solid feedstock is converted into a gas streamand a solid stream, a gas storage bladder to receive the gas stream anda receiver to receive the solid stream.

In some embodiments, the present disclosure provides, a method fordevolatizing a solid feedstock, comprising carbon-based waste selectedfrom the group consisting of hazardous material, biomass, animal manure,tires, municipal solid waste and refuse derived fuel, wherein the methodcomprises: contacting the solid feedstock with a heated gas, comprisinghydrogen at a temperature of about 500° C. to about 1000° C., injectedinto a jacketed system, whereby the solid feedstock is converted into agas stream and a solid stream.

In some other embodiments, the present disclosure provides a device fordevolatizing a solid feedstock, comprising carbon-based waste selectedfrom the group consisting of hazardous material, biomass, animal manure,tires, municipal solid waste and refuse derived fuel, wherein the devicecomprises: a chamber for contacting the solid feedstock with a heatedgas, comprising hydrogen at a temperature of about 500° C. to about1000° C.; and an injector for injecting the heated gas into the chamber;whereby the solid feedstock is converted into a gas stream and a solidstream.

In yet other embodiments, the present disclosure provides a mixture,comprising: a heated gas, comprising hydrogen at a temperature of about500° C. to about 1000° C.; and a solid feedstock, comprisingcarbon-based waste selected from the group consisting of hazardousmaterial, biomass, animal manure, tires, municipal solid waste andrefuse derived fuel, wherein the solid feedstock has an average watercontent of about 10 wt. % to about 15 wt. %.

Other features and iterations of the disclosure are described in moredetail below.

BRIEF DESCRIPTION OF THE DRAWINGS

Example embodiments are illustrated in referenced figures of thedrawings. It is intended that the embodiments and figures disclosedherein are to be considered illustrative rather than limiting.

FIG. 1 depicts the process of devolatizing a feedstock, beginning with aconditioned feedstock that is passed through a hammermill, a compactionscrew auger, and then through a devolatization unit. Followingpyrolysis, the solid stream is separated from the gas stream.

FIG. 2 depicts an assembly within the devolatization unit, comprising anauger and a retort having a recirculation sidearm.

FIG. 3 depict a gas recirculation system connected to the devolatizationunit.

FIGS. 4A & 4B further depict a gas recirculation system connected to thedevolatization unit.

DETAILED DESCRIPTION OF THE INVENTION

The present disclosure provides a method and device for injecting aheated gas into the devolatization zone of a process retort, wherein thegas comprises varying amounts of hydrogen. By injecting the heated gasinto this zone, additional energy is added to the devolatization processand a higher percentage of methane is formed in the output gas streamthan in conventional devolatization systems. Unlike typical pyrolyticprocesses, the disclosed method allows pyrolysis of the feedstockthrough direct heating with heated gas, providing a relatively compactand efficient process. Thus, these systems offer advantageousmodularity, scalability, portability, and quick installation, with loweroperating costs and higher efficiency over previous systems.

(I) Devolatization Unit and Installation

The devolatization system may be used to reduce the amount MSW. Due tothe rising costs and environmental impacts of landfills for MSW,municipalities are increasingly looking for other solutions for theirwaste disposal needs. The systems provided herein take a costly expenseand turn it into a revenue source by using the MSW as a carbon-basedfeedstock to generate clean energy. Also, globally, agricultural wasteis a major environmental concern, and may be expensive to transport anddispose. Having a modular unit near the site of agricultural wastegeneration would avoid transportation of this waste and provide energyto the local area. A system provided herein provides a solution forthese concerns and produces energy that can be resold or utilized tofuel the agricultural enterprise. Moreover, manufacturers with a highlevel of carbon-based manufacturing waste or significant energy needsmay use a system described herein to cut both their waste disposal,transportation and energy costs.

A single devolatization unit according to the present disclosuretypically produces a net output of about 1 to about 2 MW of power, forexample approximately 1.25 MW of power based on a normal mixture ofwaste from both urban and suburban households. For example to produce 5MW, four individual devolatization units are required (4 units×1.25 MW=5MW). Total energy output may be determined by multiplying power outputby the amount of time it has been producing this power. For example, if5 MW outputs used for 24 hours/day, then the total is 120 MWh of energyin a day (24 h×5 MW=120 MWh/day).

An individual devolatization unit may process from about 5 tons to about50 tons of solid feedstock per day, for example, from about 10 tons toabout 40 tons, from about 20 tons to about 30 tons, from about 5 tons toabout 10 tons, from about 10 tons to about 15 tons, from about 15 tonsto about 20 tons, from about 20 tons to about 25 tons, from about 25tons to about 30 tons, from about 30 tons to about 35 tons, from about35 tons to about 40 tons, from about 40 tons to about 45 tons, or fromabout 45 tons to about 50 tons.

Total installation size may be about 0.5 hectares (about 5,000 m²),including a feedstock segregation and preparation hall, temporarystorage for disqualified elements, miscellaneous space for plumbing andgas manifolds, office space, vehicle storage, etc. The technologicalpart of the installation requires about 180 m², including finalfeedstock preparation, devolatization unit, receiving and cooling thesyngas and carbon, and the generator set. Under the installation, anabout 20-cm thick concrete floor is recommended.

In reference to the devolatization unit, “mobile” means that the systemcan be dismantled, moved to a different location, and be operationalwithin about 30 days, for example within about 25 days, within about 20days, within about 15 days or within about 10 days. The devolatizationunit may be skid-mounted so it can be moved with a tractor/trailer.

A biological air filtration system may be installed to change the airfrequently, for example about every 10 minutes, collecting moisture andeliminating odors, thereby allowing for comfortable and clean air. Dust,odor, and debris emissions may be minimized in the process facility bymaintaining a negative air pressure in the entire waste receiving andprocessing area. Fresh air may be continuously introduced.

(II) Feedstock

Solid feedstock for the process may be any carbonaceous material,including, but are not limited to, any waste materials, coal, heavyoils, biomass and agricultural wastes. Waste materials include, but arenot limited to, automotive shredder residue, municipal solid waste(MSW), tire derived fuel (TDF), animal manure (rendered plant remains),nuts (including hulls and shells), coconut shells, seeds (e.g., corn,rice), wood, treated wood waste, fibers, compost, paper, plastic, spentactivated carbon, carpet, packing wastes, yard waste, demolition debris,roofing materials, resins, contaminated soils, spent foundry sand, spentabsorbents, sewage grit, and crop residues. Wood may be selected fromthe group consisting of bark, chips, sawdust, plywood, particle board,pallets, skids, bush, tree branches, and yard waste. Fibers may beselected from the group consisting of corrugated cardboard, newspaper,packaging, box board, aseptic board, and pulp sludge.

MSW may contain a wide variety of waste or discarded material. Forinstance, the waste may include biodegradable waste, non-biodegradablewaste, ferrous materials, non-ferrous metals, paper or cardboard invarious forms, plastic (some of which may contain trace toxic metalsthat were used as catalysts, stabilizers or other additives), paints,varnishes and solvents, fabrics, wood products, glass, chemicalsincluding medicines, pesticides and the like, solid waste of varioustypes and a wide range of other materials. The waste includes householdwaste and industrial waste, the latter being so-called “safe” industrialwaste; that is, low in toxic or hazardous materials. Raw MSW typicallyhas a fuel value of approximately 2,500 BTU per pound (5,800 kJ/kg).Processed (dried) municipal solid waste typically has a fuel value ofapproximately 4,000 BTU per pound (9,300 kJ/kg) to approximately 7,000BTU per pound (16,300 kJ/kg).

Tire-derived fuel (TDF) is composed of shredded tires. Tires may bemixed with coal or other fuels, such as wood, to be burned in concretekilns, power plants, or paper mills. TDF is usually consumed in the formof shredded or chipped material with most of the metal wire from thetire's steel belts removed. This fuel has very high energy content, withan average heat value of about 15,500 BTU per pound (36,000 kJ/kg),which is roughly the same average heat value as heavy petroleum fueloils. Fuel begins to burn at about 550° F. (290° C.) to about 650° F.(340° C.). Complete combustion is achieved with flame temperatures ofabout 1,200° F. (650° C.). Environmental concerns about this fuel focuson the chemical contents of the tire other than hydrocarbons. Ash maycontain a large mass percentage of iron, along with zinc, chromium,cadmium and lead. Calcium may be present in significant quantity.Fluorine, chlorine, sulfur, and nitrogen may comprise the bulk of thenon-metal content of the ash.

Refuse-derived fuel (RDF) or solid/specified recovered fuel (SRF) is afuel produced by shredding and dehydrating MSW. RDF consists largely ofcombustible components of municipal waste such as plastics andbiodegradable waste. RDF processing facilities are normally located neara source of MSW and, while an optional combustion or devolatizationfacility may be close to the processing facility, it may also be at aremote location. Production of RDF may involve the following steps:preliminary liberation, size screening, magnetic separation, coarseshredding, and refining separation. The residual material may be sold inits processed form or it may be compressed into pellets, bricks or logsand used for other purposes either stand-alone or in a recursiverecycling process. Advanced RDF processing methods, for examplepressurized steam treatment in an autoclave, may remove or significantlyreduce harmful pollutants and heavy metals.

The contamination level of solid feedstock depends on its origin.Assuming normal suburban landfill material without toxic waste, solidfeedstock is relatively clean and inert. Therefore, the material may besent to a landfill without further processing. For heavy metal or otherinorganic impurities, the material may be sequestered or post-processedto both purify the resulting carbon and inorganic compounds, which mayhave commercial value. Alternatively, if the concentration of inorganiccompounds is sufficiently low or benign, MSW containing the impuritiesmay be mixed with other MSW to lower the concentration of inorganicimpurities to acceptable levels. Any strategy depends on the impurity,the concentration in the MSW and the available facilities.

(III) Method and Device for Pyrolyzing a Solid Feedstock

The process for pyrolyzing a solid feedstock comprises three mainphases: feedstock preparation, devolatization, and products and energygeneration. These phases may be performed at separate locations and neednot occur in tandem. In an exemplary embodiment, devolatization occurswithin the same installation as feedstock preparation and products andenergy generation.

(a) Phase 1—Feedstock Preparation

If the feedstock is not already in a suitable condition fordevolatization (e.g., having suitable water content, particle size,substantially free of metal and non-fuel materials), it must beconditioned before devolatization. Generally, feedstock preparation maybe characterized as conversion of MSW into RDF.

The MSW passes over a segregation transmission belt. Hazardous waste isseparated and, optionally, recyclable products may be separated and sentto a recycling plant. The sorting system may maximize manual labor, becompletely automated, or be a combination of manual labor andautomation. For example, sorting systems may be fabricated with heavysteel pans and conveyor belts and equipped with productivity-enhancedfeatures such as interval switches, variable speed self-cleaning sortingbelts, overload disconnects, and electronic eyes. The system may befully interlocked with programmable logic controllers (PLC) to controlall the safety devices such as photo-cells, limit switches and flowswitches. The PLCs can be set up to control the start up and shut downsequences. The whole system can be tied into a distributed controlsystem (DCS) and controlled by a main computer.

To obtain shredded tires, tires may be split and baled to remove allwater and debris from the tires. The tires may then shredded usingmethods under ambient or cryogenic conditions. The shredded tirestypically consist of sharply cut chips, averaging less than 2.5 cm×2.5cm in size. The steel reinforcing used in tires may or may not beremoved.

Following sorting and segregation of the solid feedstock, the remainingmaterial may be passed over a transportation system to a comminutingdevice, such as a grinder, mill, shredder, or combinations thereof. Insome embodiments, the transportation system may comprise atransportation belt or conveyor belt consists of two or more pulleys,with a continuous loop of material that rotates about them. In thiscase, one or both of the pulleys are powered, moving the belt and thematerial on the belt forward. In other embodiments, the solid feedstockmay be transported using dense phase air transport.

The grinder/mill comminutes the solid feedstock by grinding, millingand/or shredding the solid feedstock, resulting in a size of about 1 cm³to about 100 cm³, for example about 5 cm³ to about 75 cm³, about 10 cm³to about 50 cm³, about 1 cm³ to about 10 cm³, about 10 cm³ to about 20cm³, about 20 cm³ to about 30 cm³, about 30 cm³ to about 40 cm³, about40 cm³ to about 50 cm³, about 50 cm³ to about 60 cm³, about 60 cm³ toabout 70 cm³, about 70 cm³ to about 80 cm³, about 80 cm³ to about 90cm³, or about 90 cm³ to about 100 cm³. In an exemplary embodiment, thesolid feedstock is comminuted to a size of about 25 cm³, or particleswith dimensions of about 5 cm by about 5 cm by about 1 cm. Other sizesmay be selected by altering the specification of the grinder and mill.These ranges are preferred because they allow efficient devolatizationof the solid feedstock.

Many devices are suitable for the comminuting process. In someembodiments, the grinder/mill may be a high-torque roller, which shredsthe solid feedstock using high-torque low-speed grinding rollers drivenwith an electric motor and are very quiet, dust-free, and self-feeding.In other embodiments, the grinder/mill may be a drum grinder. Drumgrinders comprise mechanisms consisting of a large steel drum powered bya motor, usually by means of a belt. The drum is mounted parallel to thehopper and spins towards the output chute, thus also serving as a feedmechanism. Drum grinders may be digitally controlled, reversiblehydraulic feed wheels and muffling systems. Drum chippers may have amaterial capacity of about 6 inches to about 20 inches (about 15 cm toabout 50 cm).

In other embodiments, the grinder/mill may comprise a steel disk withknives mounted on it as the grinding/milling mechanism. Reversiblehydraulically powered wheels may draw the material from the hoppertowards the disk, which is mounted perpendicularly to the incomingmaterial. As the disk spins, the knives cut the material into chips,which are thrown out the chute by flanges on the drum. A disk grindermay not be as energy-efficient as a drum grinder, but the solidfeedstock is typically comminuted to a more uniform shape and size.

Larger grinder/mills may be used for processing larger solid feedstock,for example for processing wood with diameters of about 2 feet (61 cm)to about 6 feet (180 cm). These larger grinder/mills may employ drums,disks or combinations thereof. In some embodiments, the grinder/mill isa tub grinder, which may handle a material diameter of about 8 feet (240cm) or more, and may use carbide-tipped flail hammers to pulverize thesolid feedstock rather than cut it. These grinder/mills may have anabout 200 horsepower (150 kW) to an about 1,000 horsepower (750 kW)engine. Optionally, the grinder/mill may be equipped with ananti-jamming feature.

Blades in the grinder/mill may be rectangular in shape and may be about4 inches (10 cm) to about 1.5 inches (3.8 cm) in width by about 6 inches(15 cm) to about 12 inches (30 cm) in length. Blades may have athickness from about 1.5 inches (3.8 cm) to about 2 inches (5.1 cm).Blades may be composed of any suitable resilient material, such asmetal, for example, a high grade steel and with an optional chromiumcontent of at least about 8% to enhance material hardness. In someembodiments, the blades are tipped with a carbide, such as tungstencarbide or titanium carbide.

The comminuted solid feedstock from the grinder/mill may pass through aferrous magnetic separator, where any ferrous metals may be separated.The ferrous-free waste passes through non-ferrous magnetic separator,where any aluminum or other non-ferrous metals may be separated. Theseparated ferrous metal may be placed into ferrous metal bin and anynon-ferrous metal may be placed into non-ferrous metal bin. Theremaining waste may be sent to a drying system and/or hammermill via aconveyor belt for further processing.

In some embodiments, a drying system may be integrated into theinstallation. The drying system uses heat to reduce the water contentfor the solid feedstock to a level suitable for devolatization. Watercontent varies based on the origin of the solid feedstock. If the watercontent is too high, heat added for devolatization results in drying andnot pyrolysis, thus reducing the efficiency of the process. To attainefficient devolatization, the solid feedstock may be, for example, driedto about 1 wt. % to about 15 wt. % of water in the solid feedstock, suchas about 5 wt. % to about 15 wt. %, about 10 wt. % to about 15 wt. %,about 1 wt. % to about 2 wt. %, about 2 wt. % to about 3 wt. %. about 3wt. % to about 6 wt. %, about 3 wt. % to about 4 wt. %, about 4 wt. % toabout 5 wt. %, about 5 wt. % to about 6 wt. %, about 6 wt. % to about 7wt. %, about 7 wt. % to about 8 wt. %, about 8 wt. % to about 9 wt. %,about 9 wt. % to about 10 wt. %, about 10 wt. % to about 11 wt. %, about11 wt. % to about 12 wt. %, about 12 wt. % to about 13 wt. %, about 13wt. % to about 14 wt. %, or about 14 wt. % to about 15 wt. %. The dryingsystem may be waste heat from the generator set, industrial boiler,devolatization unit, or other process in the installation to augmentheat supplied to the drying system.

(b) Phase 2—Devolatization

After the solid feedstock is conditioned to have a suitable particlesize and water content, it is sent through a jacketed system having adevolatization unit. Referring to FIG. 1, the solid feedstock 10 istransported to hopper 30, which conveys the feedstock 10 along conveyer35 to a hammermill 40 or other size reducing technology. Next, feedstock10 is compacted to a suitable density on an auger 50, for example acompaction screw auger or a vacuum auger. Compaction may also serve inthe pre-feed auger to maintain a plug of material to seal off theprocess from the environment, thereby reducing the oxygen content in thesolid feedstock. The compacted feedstock is stored in a bulk feed hopper55 until it is fed into the jacketed system 60, comprising at least onedevolatization unit having a process retort. The burner system 85 mayrecirculate output gas into the devolatization zone of the processretort.

A hammermill is a machine which further comminutes a solid feedstock byshredding or crushing the solid feedstock into smaller pieces. Thehammermill further reduces the average particle size of the solidfeedstock to provide a size unification mechanism for the solidfeedstock. The hammermill may be a steel drum containing a vertical orhorizontal rotating shaft or drum on which hammers are mounted. Thehammers may be free to swing on the ends of the rotating shaft, or fixedto the central rotor. The rotor is spun at a high speed inside the drumwhile the solid feedstock is fed into a feed hopper. The solid feedstockis impacted by the hammer bars and is thereby shredded and expelledthrough screens in the drum of a selected size. The hammermill may beused as a primary, secondary or tertiary crusher while processing asolid feedstock. In some embodiments, the hammermill is a screenlesshammermill, which uses airflow to separate smaller particles of solidfeedstock from larger particles. The screenless hammermill may be morereliable, less expensive and more energy efficient than traditionalhammermills.

Following processing through a hammermill, the solid feedstock is passedto an auger, such as a compaction screw auger (auger compactor) or avacuum transportation auger. In a compaction screw auger, athree-dimensional shredding action may significantly reduce volume ofthe feedstock. In some embodiments, the compaction screw auger may use asingle large-pitch compression screw that, unlike the back-and-forthaction of ram units, is continually moving forward, reducing processingtime and energy costs, and leaving no drag-back residue in theprocessing chamber. The solid feedstock flows one direction, eliminatingspring-back by applying constant pressure against the compacted materialin the receiving container. The continuous forward motion of the augerprocesses waste quickly with no need for hydraulics and with less energythan a ram compactor. The solid feedstock is compacted into pellets ofsuitable density for devolatization which are conveyed to a jacketedsystem.

The flow rate through the compactor is about 5 kg to about 30 kg ofsolid feedstock per minute, such as about 5 kg to about 10 kg perminute, about 10 kg to about 15 kg per minute, about 15 kg to about 20kg per minute, about 20 kg to about 25 kg per minute, or about 25 kg toabout 30 kg per minute. The solid feedstock is moved through thecompactor at a pressure of about 0.5 atm to about 3 atm, such as fromabout 1 atm to about 2 atm. Following compaction, the solid feedstockmay have a density equivalent to about 80% of the Modified Proctorscale, for example to about 90% of the Modified Proctor scale, or toabout 95% of the Modified Proctor scale. The original Proctor test, ASTMD698/AASHTO T99, uses a 4-inch-diameter (100 mm) mould which holds1/30^(th) cubic foot of solid feedstock and calls for compaction ofthree separate lifts of solid feedstock using 25 blows by a 5.5 lbhammer falling 12 inches, for a compactive effort of 12,400 ft-lbf/ft³.The “Modified Proctor” test, ASTM D1557/AASHTO T180, uses the same mouldas the standard test, but uses a 10 lb. hammer falling through 18inches, with 25 blows on each of five lifts, for a compactive effort ofabout 56,000 ft-lbf/ft³.

The jacketed system comprises a devolatization unit. The devolatizationunit has an input chamber which receives the feedstock, a conduit forheated gas (e.g., pyrolysis gas or syngas) which mixes with the solidfeedstock in the input chamber, and an output chamber where the gasstream is separated from the solid stream. Referring to FIG. 1, heat forpyrolysis is supplied to the jacketed system 60 is supplied directlyfrom a burner system 85 that receives fuel from a gas storage bladder 80through a check valve 81. The jacketed system also receives heat fromthe heated gas. Heated gas is also injected into the jacketed system. Insome embodiments, the jacketed system further comprises an injectorhaving an injection ring designed to project the heated gas into thedevolatization zone. In other embodiments, the retort may be indirectlyheated by a series of burners. These same burners may supply the energyto heat the heated gas to be circulated into the retort for thehydropyrolysis portion of the devolatization process.

As the temperature of the solid feedstock increases, pyrolysis takesplace. During pyrolysis the feedstock is thermally decomposed to releasetars, phenols, and light volatile hydrocarbon gases while the feedstockis converted to char. Depending on the origin of the feedstock, thevolatile gases may include water, hydrogen (H₂), nitrogen (N₂), oxygen(O₂), carbon dioxide (CO₂), carbon monoxide (CO), methane (CH₄),hydrogen sulfide (H₂S), ammonia (NH₃), propane (C₂H₆), and very lowlevels of unsaturated hydrocarbons such as acetylenes, olefins,aromatics and tars. Once a solid feedstock is converted to a gas stream,undesirable substances such as sulfur compounds and ash may be removedfrom the gas.

Devolatization is more effective than gasification at least because nocombustion releases or forms noxious compounds. Devolatization may be acombination of pyrolysis (devolatization in a non-oxygen atmosphere) andhydropyrolysis (devolatization in a hydrogen-enriched atmosphere).Pyrolysis is the indirect heating of materials where no flame comes intodirect contact with the material being processed. Since the reactiontakes place is a non-oxygen environment, the volatile part of thematerial is freed in the form of hydrocarbons that reform into mostlymethane.

The ratio of hydrogen to methane in the heated gas may be from about 1:1to about 1:3, for example about 1:1.5 to about 1:2.5, or about 1:2. Inan exemplary embodiment, the ratio of hydrogen to methane in the heatedgas is about 1:2. The heated gas may have a hydrogen concentration ofabout 5% to about 60%, for example, about 5% to about 10%, about 10% toabout 20%, about 20% to about 30%, about 30% to about 40%, about 40% toabout 50%, or about 50% to about 60%. In an exemplary embodiment, theheated gas has a hydrogen concentration of about 10% to about 45%. Inanother exemplary embodiment, the heated gas has a hydrogenconcentration of about 15% to about 20%. The heated gas may have apressure of about 0.5 atm to about 5 atm, for example about 0.5 atm toabout 2 atm, about 1 atm to about 2 atm, about 2 atm to about 3 atm,about 3 atm to about 4 atm, or about 4 atm to about 5 atm. In anexemplary embodiment, the heated gas has a pressure of about 0.5 atm toabout 2 atm. The temperature of the heated gas and the devolatizationunit are each about 500° C. to about 1200° C., for example about 600° C.to about 1100° C., from about 700° C. to about 1000° C., from about 800°C. to about 900° C., from about 500° C. to about 800° C., about 500° C.to about 600° C., from about 600° C. to about 700° C., from about 700°C. to about 800° C., from about 900° C. to about 1000° C., from about1000° C. to about 1100° C., or from about 1100° C. to about 1200° C. Inan exemplary embodiment, the temperature of the heated gas is about 850°C. and the temperature of the devolatization unit is about 850° C. Thelength of the devolatization zone may be about 3 feet to about 24 feet(about 1 meter to about 8 meters), for example about 3 feet to about 6feet (about 1 meter to about 2 meters), about 6 feet to 9 feet (about 2meters to about 3 meters), about 9 feet to about 12 feet (about 3 metersto about 4 meters), about 12 feet to about 15 feet (about 4 meters toabout 5 meters), about 15 feet to about 18 feet (about 5 meters to about6 meters), about 18 feet to about 21 feet (about 6 meters to about 7meters), and about 21 feet to about 24 feet (about 7 meters to about 8meters). In an exemplary embodiment, the devolatization zone is about 6feet to about 12 feet (about 2 meters to about 4 meters), or about 9feet (about 3 meters). The length of path of travel for the solidfeedstock through the jacketed system may be about 9 feet to about 90feet (about 3 meters to about 30 meters), for example about 18 feet toabout 63 feet (about 6 meters to about 21 meters), about 27 feet toabout 54 feet (about 9 meters to about 18 meters), 9 feet to about 18feet (about 3 meters to about 6 meters), about 18 feet to about 27 feet(about 6 meters to about 9 meters), about 27 feet to about 36 feet(about 9 meters to about 12 meters), about 36 feet to about 45 feet(about 12 meters to about 15 meters), about 45 feet to about 54 feet(about 15 meters to about 18 meters), about 54 feet to about 63 feet(about 18 meters to about 21 meters), about 63 feet to about 72 feet(about 21 meters to about 24 meters), about 72 feet to about 81 feet(about 24 meters to about 27 meters), or about 81 feet to about 90 feet(about 27 meters to about 30 meters). In an exemplary embodiment, thelength of path of travel for the solid feedstock through the jacketedsystem may be about 45 feet (about 15 meters).

Feedstock entering the system should be permitted time to devolatizecompletely, for example about 1 second to about 300 seconds, such asabout 30 seconds to about 240 seconds, or about 60 seconds to about 120seconds. Any portion of feedstock must be exposed to sufficient energyinput effect pyrolysis or hydropyrolysis. Solid feedstock which isinsufficiently comminuted, too large, or is tightly packed may not havesufficient time and exposure to heat to completely devolatize.

In some embodiments, a turbocharging pump doses a predetermined amountof heated gas to the devolatization unit. In an exemplary embodiment, ahydropyrolysis loop is configured with an enhanced blower and augerretort. Referring to FIG. 2, retort 61 is equipped with an auger 62 anda sidearm 63. The auger 62 sized to fit within the inner cavity of theretort 61. The sidearm recirculates excess heated gas, for examplepyrolysis gas enriched with hydrogen which was used in previousiterations of the devolatization process and, optionally, transportsproduct gas back into the retort. As a result of the closed-loop system,there are no emissions.

Referring to FIG. 3, the heated gas recirculation system 300 optionallyreceives the gas stream from the jacketed system 60 which may be sent toa clean-up train 75, comprising a first cyclone 72, a second cyclone 73and an auger 71. In a particular embodiment, the cyclones 72, 73separate the solid stream from the gas stream, sending the solid streaminto auger 71. In other embodiments, the gas stream may be sent to adeduster, in which lightweight particulate matter are removed in the gasstream.

Referring to FIGS. 3 and 4, the gas stream may be stored in a gasstorage bladder (for example as depicted in FIG. 1). Alternatively, thegas stream may be recirculated from the clean-up train 75 into thejacketed system 60 toward plenum 62 in return pipe 76 using a blowersystem 77. The flow and pressure of the gas stream into the jacketedsystem 60 may be controlled with a pressure regulator 78 and a valve 79.The high compression blower 77 may take the gas received from theclean-up train 75 at about 2 psi to about 5 psi and further compressesthe clean gas to about 5 psi to about 10 psi. Once the clean compressedgas enters the heated portion of the plenum 62 in the jacketed system60, the gas is immediately heated to process temperature of the retort61. In an exemplary embodiment, the gas stream is continually injectedinto the jacketed system 60 due to the rapid expansion of gas. In someembodiments, the heated gas provides the hydropyrolysis portion of theprocess, while the indirect heating of the solid feedstock from theburner system 85 provides the pyrolysis portion of the process.

Cyclones 72, 73 operate under the principle of cyclonic separation, amethod of removing particulates from a gas stream, without the use offilters, through vortex separation. Rotational effects and gravity areused to separate mixtures of solids and gas. A high speed rotatingairflow is established within a cylindrical or conical containerreferred to as a cyclone. The gas stream flows in a helical pattern,beginning at the top (wide end) of the cyclone and ending at the bottom(narrow) end before exiting the cyclone in a straight stream through thecenter of the cyclone and out the top. Denser particles in the rotatingstream have too much inertia to follow the tight curve of the stream,thus striking the outside wall and falling to the bottom of the cyclonewhere they may be removed. In a conical system, as the rotating flowmoves towards the narrow end of the cyclone, the rotational radius ofthe stream is reduced, thus separating smaller and smaller particles.The cyclone geometry, together with flow rate, defines the cut point ofthe cyclone; this is the size of particle that will be removed from thestream with an about 50% efficiency. Particles larger than the cut pointare removed with a greater efficiency and smaller particles with a lowerefficiency. In some embodiments, a secondary airflow within the cyclonemay keep the collected particles from striking the walls, thusprotecting the walls from abrasion. The primary air flow containing theparticulates enters from the bottom of the cyclone and is forced intospiral rotation by stationary spinner vanes. The secondary air flowenters from the top of the cyclone and moves downward toward the bottom,intercepting the particulate from the primary air. The secondary airflow also allows the collector to optionally be mounted horizontally,because it pushes the particulates toward the collection area, and doesnot rely solely on gravity to perform this function.

(c) Phase 3—Product Streams and Energy Production

In some embodiments, gas and solid product streams result from thedevolatization process. Energy may be generated by combusting the gasstream or the solid stream. Referring again to FIG. 1, the solid streammay be sent to a receiver 70 where the solid stream is further separatedfrom the gas stream, sending the solid stream to containers 75 forsecondary uses. The gas stream may pass through a check valve 81 to astorage bladder 80, or it may be recirculated in the jacketed system(for example, as depicted in FIGS. 2-4).

Referring to FIG. 1, from storage bladder 80, the gas stream may be sentalong pipe 82 to burner system 85 operatively connected to the jacketedsystem 60. In burner system 85, the gas stream is combusted to providethermal energy to the jacketed system for the devolatization process.Alternatively, the gas stream may be moved from storage bladder 80 alongpipe 83 to generator set 90, providing fuel of energy generation. In yetother embodiments, the gas stream may be moved from storage bladder 80along pipe 83 to a process boiler 95 or to another industrial processuse 97. Exemplarily, waste heat from generator set 90 of process boiler95 may be used for drying the solid feedstock earlier in the process, asdescribed above, or may also provide a secondary heat source of thedevolatization reaction.

In some embodiments, the devolatization installation comprises an energyand power generation set. Brand and size of the generator set (engineand generator) may be selected based on the needs of the user.Caterpillar and Cummins Power are examples of brands which may producedand supply a generator set.

The solid stream produced from the devolatization of solid feedstock maybe cooled and received. In an exemplary embodiment, the solid stream isseparated with a cyclone and transported with an auger to a container.The size of the storage container depends on the amount of solid streamproduced, which is a function of the composition of the solid feedstock.Following devolatization, the solid stream comprises materials that havea significantly higher concentration of carbon than the solid feedstock,such as coke, char, charcoal, activated carbon, semi-activated carbon,and carbon black. These carbon-rich materials of the solid stream may beused as soil amendments, fuel, filler for rubber, in plastics, or as afiltering aids and additives for road-surfacing materials, and may havevarying porosity and surface areas.

In some embodiments, clean grit, long-chain hydrocarbons (oils) or tarsmay be produced as part of the solid stream. These materials may becollected separately from the carbon-enriched material of the solidstream and may be sold to the chemical and pharmaceutical industries. Insome embodiments, long-chain hydrocarbons and tars may be mixed withsolid feedstock and recirculated through the devolatization system.

Following devolatization, the solid feedstock produces a gas stream. Thegas stream is flammable and may contains a similar distribution ofchemicals as natural gas, but with a lower average methaneconcentration: about 0% to about 20% hydrogen, about 20% to about 70%methane, and about 30% total of nitrogen, ethane, propane, butane,carbon monoxide, and carbon dioxide, optionally with other trace gases.In exemplary embodiments, gas streams with a hydrogen content arerecirculated into the jacketed system, providing heated gas that aids indevolatization of the solid feedstock.

In other exemplary embodiments, the gas stream comprises a greatermethane content than gas streams produced from conventionaldevolatization processes. While standard natural gas consistsessentially of methane, the gas stream from devolatization of a solidfeedstock comprises at least about 20% methane, for example at leastabout 30% methane, at least about 40% methane, at least about 50%methane, or from about 60% to about 70% methane. In a particularembodiment, the remaining gases in the gas stream are nitrogen andcarbon dioxide, which pass through the power generator unburned andunmodified. Like the solid stream, composition of the gas stream is afunction of the solid feedstock. In some embodiments, the gas streamincludes synthesis gas (syngas), which is a mixture of hydrogen andcarbon monoxide. Syngas may be used for power production or used forother industrial purposes.

About 10% to about 15% of the gas stream may be used for energygeneration which powers the installation. Optionally, up to about 10% ofthe gas stream may be reinjected into the devolatization zone of theprocess retort as a heated gas, advantageously providing thermal energyto aid devolatization of the solid feedstock. The remaining about 85% toabout 90% of the gas stream may be cooled and stored in a gas bladder.The gas stream may have a calorific value of about 400 BTU per cubicfeet to about 1000 BTU per cubic feet, for example from about 500 BTUper cubic feet to about 900 BTU per cubic feet, from about 600 BTU percubic feet to about 800 BTU per cubic feet, from about 400 BTU per cubicfeet to about 500 BTU per cubic feet, from about 500 BTU per cubic feetto about 600 BTU per cubic feet, from about 600 BTU per cubic feet toabout 700 BTU per cubic feet, from about 700 BTU per cubic feet to about800 BTU per cubic feet, from about 800 BTU per cubic feet to about 900BTU per cubic feet, or from about 900 BTU per cubic feet to about 1000BTU per cubic feet. In an exemplary embodiment, the gas stream has acalorific value of about 600 BTU per cubic feet to about 750 BTU percubic feet. For the sake of comparison, standard natural gas has anaverage value of about 1000 BTU per cubic feet.

Definitions

“Gasification” generally refers to a process that enables the productionof a combustible or synthetic gas (e.g., a gas comprising H₂, CO, CO₂and CH₄) from a carbon-based feedstock, referred to as carbonaceousfeedstock or a solid feedstock. The gas may be used to generateelectricity or as a basic raw material to produce chemicals and liquidfuels. In particular, the gas may be used for combustion in a boiler forthe production of steam for internal processing and/or other externalpurposes: the generation of electricity through a steam turbine; thecombustion directly in a gas turbine or a gas engine for the productionof electricity; fuel cells; the production of methanol and other liquidfuels; as a further feedstock for the production of chemicals such asplastics and fertilizers; the extraction of both hydrogen and carbonmonoxide as discrete industrial fuel gases; and other industrial heatrequirements as required.

Most processes that are either updraft or downdraft gasification systemsare considered starved air gasification or starved air combustion. Bystarving or limiting the air into a thermal combustion, the material isallowed to break down into carbon, oxygen and hydrogen to reform into COand H₂. If too much air is allowed the product, of that combustionconsists essentially of CO₂ and water with substantially no BTU value.In starved air combustion, CO and H₂ form a gas that may be combusted orreformed into syngas. Therefore, since starved air combustion iscombustion, only ash remains after the process.

When introducing elements of the present disclosure or the exemplaryembodiments(s) thereof, the articles “a”, “an”, “the” and “said” areintended to mean that there are one or more of the elements. The terms“comprising”, “including” and “having” are intended to be inclusive andmean that there may be additional elements other than the listedelements.

Having described the disclosure in detail, it will be apparent thatmodifications and variations are possible without departing from thescope of the disclosure defined in the appended claims.

EXAMPLES

The following example is included to demonstrate embodiments of thedisclosure, in particular use of a heated gas to devolatize (pyrolyzeand hydropyrolyze) a solid feedstock comprising municipal solid waste(MSW). It should be appreciated by those of skill in the art that thetechniques disclosed in the examples represent techniques discovered bythe inventors to function well in the practice of the disclosure. Thoseof skill in the art should, however, in light of the present disclosure,appreciate that many changes may be made in the specific embodimentsthat are disclosed and still obtain a like or similar result withoutdeparting from the spirit and scope of the disclosure, therefore allmatter set forth is to be interpreted as illustrative and not in alimiting sense.

MSW was processed to remove non-combustible items. Specifically,non-combustible items such as glass and metals (aluminum, steel, ironand tin) and items that may be recycled were removed mechanically fromthe MSW on a segregation transmission belt. Next, the sorted MSW wasconveyed to a grinder/mill, which comminuted the MSW to an averageparticle size of about 20 cm³ to about 30 cm³. The comminuted MSW thenpassed through a dryer system which reduced the average water content tonot more than about 15 wt. %. This sorted, comminuted, dried MSW isreferred to as refuse derived fuel (RDF).

Referring to FIG. 1, the RDF 10 was transported with a front end loader20 to a RDF reclaim hopper 30. A conveyer belt 35 transported the RDF 10to a further reduction process of various means and methods depending onthe solid feedstock (for example a hammermill 40), which furthercomminuted and homogenized the RDF. Next, conveyor belt 45 transportedRDF 10 down chute 51 to a compaction screw auger 50, where the RDF 10was compacted to pellets having a suitable density for devolatization.The compacted RDF was stored in a bulk feed hopper 55 until it was fedinto the jacketed system 60, comprising at least one devolatization unithaving a process retort. The burner system 85 heated the jacketed systemto a temperature of about 500° C. to about 850° C.

A gaseous mixture was prepared from hydrogen and methane, which wassubstantially free of oxygen and water. The gas was passed through asuperheater, which was typically used to form superheated steam, at apressure of about 0.5 atm to about 2 atm for about 1 minute. Theresulting heated gas had a temperature of about 500° C. about 850° C., apressure of about 1 atm to about 2 atm, and a hydrogen concentrationabout 10% to about 45%. At least a portion of the heated gas wasrecirculated from a previous iteration of the devolatization process.One of skill in the art would recognize that temperatures and pressuresare generally as described and may be varied depending on the solidfeedstock, including percentages and ratios of components in the gaseousmixture.

The heated gas was injected into the devolatization zone of a retort ata pressure of about 0.5 atm to about 2 atm. RDF was fed continuouslythrough the retort using an auger, providing a continuous devolatizationprocess. The RDF resided in the devolatization zone of the retort forabout 60 seconds to about 120 seconds, thus contacting the RDF with theheated gas and rapidly heating the RDF. The ratio of RDF to heated gaswas about 1 kilogram per liter (kg/L) to about 2 kg/L. Throughout theinjecting and feeding processes, the retort may be heated with one ormore burners, for example, one burner, two burners, three burners, orfour burners. One of skill in the art would also recognize that times ofdevolatization may depend on the composition of the solid feedstock.

Devolatization in the process retort produced a gas stream and acarbon-enriched material. Referring again to FIG. 1, the carbon-enrichedmaterial was sent to a receiver 70 where the material was furtherseparated from the gas stream, sending the solid stream to containers 75for secondary uses. About 90% of the gas stream passed through a checkvalve 81 to a storage bladder 80, and about 10% of the gas stream wasrecirculated into the process retort of the jacketed system 60 (asdepicted in FIGS. 2-4). Alternatively, 100% of the gas is sent to thestorage bladder. Specifically referring to FIG. 3, the heated gasrecirculation system 300 received the gas stream from the jacketedsystem 60 which was sent to a first cyclone 72 and then a second cyclone73. The cyclones 72, 73 separated the carbon-enriched material from thegas stream, sending the carbon-enriched material into auger 71. The flowof the gas stream into the jacketed system was controlled at valve 79.

About 85% to about 95% of the RDF was converted to a gas stream andabout 20% was converted to a carbon-enriched material, depending on thesolid feedstock. About 30 tons of RDF with an average calorific value ofat least about 13 GJ/ton produced about 20,400 m³ of a gas stream with atotal calorific value of about 24 MJ/m³ (650 BTU per cubic foot) toabout 28 MJ/m³ (750 BTU per cubic foot). The finished gas streamcomprises about 10% to about 20% hydrogen, about 50% to about 70%methane, and about 30% total of nitrogen, ethane, propane, butane,carbon monoxide and carbon dioxide. About 5% to about 15% of the RDF wasconverted to elemental carbon with a calorific value of about 28,000kJ/kg.

The emissions of the burners for the devolatization unit describedherein were about 0.01 mg/m³ of particulate matter, 0.002 mg/m³ ofsulfur dioxide (SO₂), about 0.03 mg/m³ of nitrogen oxides (NO_(x)),about 0.01 mg/m³ of volatile organic compounds (VOCs), about 0.2 mg/m³of carbon monoxide and about 111 g/m³ of carbon dioxide, with nodetectable dioxins or furans. The lack of oxygen and thus the lack ofcombustion during devolatization is a reason why dioxins and furans werenot products of the disclosed process. These emission concentrations areat least two orders of magnitude below the emission concentrationsrequired by the European Union. Emissions were even further minimized byoperating the devolatization unit as a closed loop system, as describedin the exemplary embodiments.

As demonstrated above, MSW is efficiently devolatized, producing avaluable gas stream and solid stream.

What is claimed is:
 1. A method for devolatizing a solid feedstock,comprising carbon-based waste selected from the group consisting ofhazardous material, biomass, animal manure, tires, municipal solid wasteand refuse derived fuel, wherein the method comprises: treating thesolid feedstock to a produce a particle size laying between 1 cm³ and100 cm³; passing the solid feedstock into a jacketed system; andcontacting the solid feedstock with a heated gas, comprising hydrogen,inside the jacketed system at a temperature of 500° C. to 1000° C. for atime of 60 seconds to 120 seconds, whereby the solid feedstock isconverted into a gas stream and a solid stream.
 2. The method of claim1, wherein the heated gas has a temperature of 500° C. to 1000° C. 3.The method of claim 2, wherein the heated gas has a temperature of 800°C. to 900° C.
 4. The method of claim 1, wherein the jacketed system forconverting solid feedstock comprises a device for moving solidfeedstock.
 5. The method of claim 4, wherein the device for moving solidfeedstock comprises: a retort having a devolatization zone; an augerdisposed within the retort; and a recirculation sidearm attached to theretort, wherein the recirculation sidearm recirculates the gas streaminto the retort.
 6. The method of claim 5, wherein the solid feedstockis contacted with the heated gas inside the devolatization zone of theprocess retort.
 7. The method of claim 6, wherein the jacketed systemfurther comprises an injector having an injection ring designed toproject the heated gas into the devolatization zone.
 8. The method ofclaim 7, wherein the solid feedstock is fed continuously through theretort using the auger.
 9. The method of claim 1, wherein the methodfurther comprises heating a gas to produce the heated gas at atemperature of 500° C. to 1000° C. and a pressure of 0.5 atm to 2 atm.10. The method of claim 1, wherein the heated gas further comprisesmethane.
 11. The method of claim 1, wherein the heated gas issubstantially free of water and oxygen gas.
 12. The method of claim 1,wherein the gas stream comprises hydrogen and carbon monoxide.
 13. Themethod of claim 1, wherein the solid stream comprises carbon-enrichedmaterial.
 14. The method of claim 13, wherein the carbon-enrichedmaterial is semi-activated carbon.
 15. A method of using a heated gas,comprising hydrogen, to pyrolyze a solid feedstock, comprisingcarbon-based waste selected from the group consisting of hazardousmaterial, biomass, animal manure, tires, municipal solid waste andrefuse derived fuel, wherein the method comprises: treating the solidfeedstock to a produce a particle size laying between 2 cm³ and 3 cm³;passing the solid feedstock into a jacketed system; and contacting thesolid feedstock with the heated gas inside the jacketed system at atemperature of 800° C. to 900° C. and a pressure of 0.5 atm to 2 atm fora time of 60 seconds to 120 seconds, whereby the solid feedstock isconverted to a gas stream and a solid stream.
 16. An installation forpyrolyzing a solid feedstock, comprising waste selected from the groupconsisting of hazardous material, biomass, animal manure, tires,municipal solid waste and refuse derived fuel, wherein the installationcomprises: A device for reducing particle size; A compaction screwauger; A device for contacting the solid feedstock with a heated gas,comprising hydrogen gas, inside a jacketed system at a temperature of500° C. to 1000° C. for a time of 60 seconds to 120 seconds, whereby thesolid feedstock is converted into a gas stream and a solid stream; a gasstorage bladder to receive the gas stream; and a receiver to receive thesolid stream.
 17. The installation of claim 16, further comprising adevice for removing non-fuel materials from the solid feedstock.
 18. Theinstallation of claim 16, wherein the device for reducing particle sizecomprises a grinder/mill to comminute the solid feedstock.
 19. Theinstallation of claim 16, further comprising a drying system to dry thesolid feedstock to an average water content of 10 wt. % to 15 wt. %. 20.The installation of claim 16, further comprising: a device for removingnon-fuel materials from the solid feedstock; a grinder/mill to comminutethe solid feedstock; and a drying system to dry the solid feedstock toan average water content of 10 wt. % to 15 wt. %.
 21. The installationof claim 16, wherein the heated gas has a temperature of 500° C. to1000° C. and a pressure of 0.5 atm to 2 atm.
 22. The installation ofclaim 21, wherein the heated gas has a temperature of 800° C. to 900° C.23. The installation of claim 16, wherein the jacketed system has atemperature of 800° C. to 900° C.
 24. The installation of claim 16,wherein the solid feedstock is reduced to a particle size laying between1 cm³ and 100 cm³.
 25. The installation of claim 24, wherein the solidfeedstock is reduced to a particle size laying between 2 cm³ and 3 cm³.26. A method for devolatizing a solid feedstock, comprising carbon-basedwaste selected from the group consisting of hazardous material, biomass,animal manure, tires, municipal solid waste and refuse derived fuel,wherein the method comprises: contacting the solid feedstock with aheated gas, comprising hydrogen at a temperature of 500° C. to 1000° C.,injected into a jacketed system, whereby the solid feedstock isconverted into a gas stream and a solid stream.
 27. A device fordevolatizing a solid feedstock, comprising carbon-based waste selectedfrom the group consisting of hazardous material, biomass, animal manure,tires, municipal solid waste and refuse derived fuel, wherein the devicecomprises: a chamber for contacting the solid feedstock with a heatedgas, comprising hydrogen at a temperature of 500° C. to 1000° C.; and aninjector for injecting the heated gas into the chamber; whereby thesolid feedstock is converted into a gas stream and a solid stream.
 28. Amixture, comprising: a heated gas, comprising hydrogen at a temperatureof 500° C. to 1000° C.; and a solid feedstock, comprising carbon-basedwaste selected from the group consisting of hazardous material, biomass,animal manure, tires, municipal solid waste and refuse derived fuel,wherein the solid feedstock has an average water content of 10 wt. % to15 wt. %.